WO2004067197A1 - 有機廃棄物処理方法、有機廃棄物処理剤およびそれに用いる微生物 - Google Patents
有機廃棄物処理方法、有機廃棄物処理剤およびそれに用いる微生物 Download PDFInfo
- Publication number
- WO2004067197A1 WO2004067197A1 PCT/JP2004/000797 JP2004000797W WO2004067197A1 WO 2004067197 A1 WO2004067197 A1 WO 2004067197A1 JP 2004000797 W JP2004000797 W JP 2004000797W WO 2004067197 A1 WO2004067197 A1 WO 2004067197A1
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- Prior art keywords
- organic waste
- bacillus
- bacterium
- mesophilic
- treating
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/20—Bacteria; Culture media therefor
- C12N1/205—Bacterial isolates
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
- C12R2001/07—Bacillus
Definitions
- the present invention relates to an organic waste treatment method using a useful microorganism, an organic waste treatment agent, and a useful microorganism used for the same.
- microorganisms to disassemble and digest these wastes, or to compost them by means of composting.
- the microorganisms involved in these degradation and digestion processes rely on spontaneous generation, and therefore require a long time to reach the concentration of microorganisms required for treatment.
- the composting of organic waste is performed in order to maintain the temperature in this process. It discloses a treatment agent containing spores of the genus Bacillus as an agent. See page 1. ).
- Patent Document 1 Japanese Patent Application Laid-Open No. 9-112387 (pages 11 and 12)
- Patent Document 2 Japanese Patent Application Laid-Open No. 7-330478 (pages 11 and 12)
- the present invention seeks to overcome the above-mentioned drawbacks of the conventional technology, and is excellent in smooth temperature rise in an initial processing stage, and has good temperature stability in a high temperature range and is stable.
- Organic waste treatment method, organic waste treatment agent, and microorganisms used in the organic waste treatment method which can achieve stable organic waste treatment effect and increase the amount of treated waste by promoting the treatment of organic waste and promoting the evaporation of water. It is intended to be provided. Disclosure of the invention The present inventors have conducted intensive studies to solve the above-mentioned problems, and as a result, have found that the above-mentioned problems can be solved by combining certain kinds of microorganisms in organic waste. did.
- the present invention is as follows.
- the mesophilic bacterium has a pyrogenic action.
- thermophilic bacterium of the waste is 1. 0 xl 0 3 ⁇ l 0 xl 0 8 CFU / g der Ru this said you wherein (1) -
- the organic waste is characterized by being garbage, livestock waste, sewage treatment-derived waste or industrial waste.
- An organic waste treatment agent characterized by containing a mesophilic bacterium having an activity at 15 to 50 ° C and a thermophilic bacterium having an activity at 50 to 70 ° C.
- thermophilic bacterium Bacillus (Bacillus) Shokudea Ru This said, wherein (1 6) or (1-7)
- thermophilic bacterium is a Bacillus' nodule.
- “having activity” means that the microorganism is not only alive but also decomposes or assimilates organic matter within a temperature range in which the microorganism can survive. It means that the bacterium itself can grow.
- the temperature of the object to be treated is rapidly increased by spontaneous heat generation by mesophilic bacteria having activity in the medium temperature range.
- the temperature rises quickly, and after reaching the optimum temperature of the thermophilic bacterium, the natural heat of the thermophilic bacterium that is active in the high-temperature region increases the efficiency of maintaining and decomposing the product temperature of the target treated material. it can.
- the stable high temperature condition further accelerates the evaporation of water contained in the target processed material, thereby enabling a reduction in the processed material.
- the temperature of the target treated material decreased due to some factors such as the addition of new waste and stirring. In this case, the seeds germinate again and the temperature is raised by starting the activity. As a result, the temperature of the object to be treated can be stabilized and a high temperature can be maintained.
- the temperature of the object to be treated can be maintained at a high temperature, and by combining strains having optimal activities according to each temperature, digestion and decomposition become more efficient and the throughput is reduced. To increase.
- FIG. 1 is a graph comparing the temperature change between a test machine using Bacillus subtilis C-13102 strain and a control device in Example 1. It is.
- FIG. 2 is a graph comparing the change in the content weight between the test device using the Bacillus subtilis C—3102 strain and the control device in Example 1.
- FIG. 3 is a graph comparing the temperature change between a test machine using Bacillus pallidus TK604 strain and a control machine in Example 2.
- FIG. 4 is a graph comparing the change in the content weight between the test machine using the Bacillus pallidus TK604 strain and the control machine in Example 2.
- FIG. 5 shows the strain of Notinoles subtilis (Bacillus subtilis) C—3102 strain and Notinoles-no in Example 3. Rita, Bacillus pallidus T ⁇
- FIG. 6 shows a test machine using Bacillus subtilis (Bacillus subtilis) C13102 strain and Notinoles-Noridas (Bacillus pallidus) TK604 strain in Example 3 and a control machine. This is a graph comparing the weight change of the contents of and. BEST MODE FOR CARRYING OUT THE INVENTION
- the mesophilic bacterium used in the present invention is not particularly limited as long as it has an activity at 15 to 50 ° C, but it has an exothermic effect of increasing the product temperature from a low temperature to a high temperature range.
- the spores are formed in a high temperature range of 50 ° C. or more.
- Spore formation is a property of self-preservation by forming highly resistant spores under conditions unfavorable for growth such as nutritional deficiency, drying or heat.
- thermophilic bacterium used in the present invention is not particularly limited as long as it has activity at 50 to 70 ° C.
- At least one of these mesophilic and thermophilic bacteria has the ability to degrade organic matter.
- the organic matter decomposing property is a property of a microorganism that decomposes and digests organic wastes such as carbohydrates, proteins, and lipids.
- organic wastes such as carbohydrates, proteins, and lipids.
- the above-mentioned exothermic effect is generated by microorganisms or microorganisms in the process of decomposing and digesting. This is the heat-generating action of the enzymes produced by the decomposition of organic waste.
- the position of the biological classification of these mesophilic and thermophilic bacteria is not particularly limited, and includes, for example, the genus Bacillus.
- the mesophilic and thermophilic bacteria of the present invention include notinoles subtilis as a bacterial species of the genus Bacillus. (B. subtilis), B. anthracis, Bacillus azotof orraans, Bacillus brevis , Bacillus' Cellus
- Bacillus stearoothermofilus Bacillus stearoothermofilus (B. steanothermophi lus), / Chinoles norrita, Bacillus pallidus, and the like.
- the mesophilic bacterium is Notillus subtilis (Bacillus subtilis), and the thermophilic bacterium is Bacillus pallidus.
- a preferred example of the mesophilic bacterium of the present invention is Bacillus subtilis C-3102.
- a liquid medium or a solid medium containing a carbon source, a nitrogen source, an inorganic substance, and the like, which are usually used for culture, can be used.
- the carbon source may be any assimilable carbon source, such as glucose, sucrose, starch, molasses, etc.
- the nitrogen source may be, for example, peptone or meat extract.
- phosphates, magnesium, sodium, salts such as potassium, calcium, iron or manganese, vitamins, amino acids, defoamers, surfactants Agents and the like can also be added.
- the culture is preferably carried out under aerobic conditions.
- the initial pH of the medium is 5 to 9, especially 6 to 8, and the culture temperature is 20 to 50 ° C, especially 35 to 40 ° C.
- the cultivation time is preferably from 12 hours to 7 days.
- thermophilic bacterium of the present invention is a novel strain, Bacillus pallidus TK604 strain.
- This strain, Bacillus pallidus TK 6004 strain was established on August 22, 2002 in Tsukuba East, Ibaraki Prefecture, Japan.
- Original deposit with the National Institute of Advanced Industrial Science and Technology at the Patent Organism Depositary at the National Institute of Advanced Industrial Science and Technology (AIST) No. 1 and deposited with the original deposit number FERMP — 18983.
- FERMP National Institute of Advanced Industrial Science and Technology
- This Bacillus pallidus TK604 strain was isolated from humus.
- TK604 strain was isolated and selected as the thermophilic bacterium of the present invention.
- thermophilic bacterium of the present invention those having strong activity at 50 ° C or higher but having no activity at 50 ° C or lower can be applied as the thermophilic bacterium of the present invention.
- thermophilic bacterium of the present invention not only the above-mentioned method but also a method of raising the temperature to about 50 ° C. in advance by other means (sterilization) Separation can also be performed by adding to raw garbage and raising the temperature to a higher temperature range by checking the presence or absence of activity at 50 ° C or higher.
- T S (Trypticase Soy Becton Dickinson, NJ U.S.A.) Agar medium:
- Attitude to oxygen aerobic, aerobic, etc.
- the 16S rDNA was analyzed for homology to closely related strains.
- the DNA information of closely related strains to be compared during the homology analysis was obtained using a data source, i.e., microSeq Bacterial Full. Gene Library v. 0001 (Applied Biosystems, USA) was used.
- the homology between the Batinoles' Paridas TK604 strain and the top 10 closely related strains is described below.
- Bacillus lentus 89.9.92%
- Bacillus stearothermophilus 89.86%
- Bacillus coagulans 89.41%
- Bacillus subtilis C is used as a medium.
- the same one used for cultivation of 3102 (FERMBP-1106) can be used.
- the culture is preferably performed under aerobic conditions, and the initial pH of the culture medium is 5 to 9, especially 6 to 8, and the culture temperature is 30 to 60 ° C, particularly 50 to 60 ° C.
- the cultivation time is preferably 12 hours to 7 days.
- thermophilic bacterium of organic waste but are not limited to, 1. 0 xl 03 ⁇ i. O xl 0 8 and this is rather preferable in the range of CFUZ g, further preferred The range is from 1.0 X 10 3 to 1.0 X 10 6 CFU ./g.
- the method of adding and adding the bacterial cells and the organic waste is not particularly limited.
- the bacterial cells may be added and injected at once, the mesophilic and thermophilic bacteria may be divided and added in multiple stages, or the mesophilic and thermophilic bacteria may be separately added and injected, respectively. You may.
- mesophilic bacteria and thermophilic bacteria are eliminated from organic waste. It is preferable to add and inject the cells at once.
- the method for adding and adding organic waste may be a method in which the waste is added and charged in a lump to a container for treatment in advance, or may be a plurality of steps. It is also possible to add the next organic waste at the stage where the previously injected organic waste is decomposed and reduced in volume to some extent.
- the form of the mesophilic bacteria and the thermophilic bacteria used for the addition and addition is not particularly limited, and a culture solution of live bacteria cultured in a liquid medium may be used as it is. Alternatively, it may be a concentrated viable cell obtained by collecting a culture of a viable cell cultured in a liquid medium by centrifugation or the like, or may be a freeze-dried cell. In addition, spores may be used as long as mesophilic bacteria and thermophilic bacteria form spores.
- the organic waste is not particularly limited, but includes garbage, livestock waste, sewage waste, and industrial waste.
- Garbage is waste that can be decomposed by organic microorganisms emitted from households and businesses.
- Livestock waste refers to organic waste such as excrement of livestock and poultry, such as cow dung and poultry dung, which are emitted by the livestock industry and processing of livestock products.
- the sewage treatment-derived waste means excess sludge discharged as a by-product from activated sludge treatment.
- Industrial waste includes the above-mentioned business-related garbage, livestock waste, waste from sewage treatment, and the like.
- the form of applying the mesophiles and thermophiles to the organic waste treatment agent according to the present invention is the same as that of the mesophilic bacteria and thermophiles used for addition in the treatment method described above. Although not particularly limited, it is a culture solution of live bacteria cultured in a liquid medium. Also, concentrated viable cells, freeze-dried cells, and spores formed by mesophilic and thermophilic bacteria obtained by centrifuging the culture solution of live bacteria cultured in a liquid medium. If so, it may be the spore.
- the test was performed using two household trash treatment machines (SANYO: SNS-M15).
- the processor has a raw trash treatment capacity of 700 g per day (manufacturer recommended amount).
- 4.5 kg (recommended amount of the manufacturer) of a manufacturer-designated whole chip (SNM-HK13) was injected, and the experiment was started.
- a thermometer temperature measurement Jr: T & D
- T & D temperature measurement
- the single garbage disposal and tester was added Bachinoresu subtilis during garbage on of the start of the experiment (Bacillus subtilis) bacterial powder 3 C one 3102 0 g (1 x 1 0 io C f uZ g).
- the other was used as a control and operated according to the manufacturer's instructions.
- 1.5 kg of garbage which is about twice the recommended amount of the manufacturer, was injected at both the test and control machines.
- the total weight of the machine was measured at the time of raw trash injection, and the daily digestibility was determined from the difference from the previous day.
- the bacterial powder is obtained by culturing live bacteria, heat-drying them, inducing spore formation of the bacteria, completely removing water, and pulverizing them.
- Figure 2 shows the change in the weight of the contents of the garbage processor.
- the vertical axis indicates the content weight (g), and the horizontal axis indicates the number of days elapsed since the start of the test.
- garbage that could not be digested continued to accumulate inside the control unit and test machine, and the internal weight continued to increase I went.
- the temperature of the test machine rose faster than that of the control machine, so that the decomposition of raw garbage proceeded, and the internal weight tended to increase slightly more slowly than in the control. Was observed.
- the internal temperature of the tester increased by 6 days.
- Figure 4 shows the change in the weight of the contents of the garbage disposal. From the fourth day when the internal temperature reached 65 ° C, the processor continued to process 1,400 g of raw garbage, almost twice the manufacturer's recommended amount. On the other hand, the control unit showed a tendency for garbage that could not be processed to accumulate inside and increase the weight of the contents. With the introduction of the thermophilic bacterium Bacillus pallidus TK6004, it was possible to treat almost twice the amount of garbage that is recommended by the manufacturer.
- thermophilic bacterium Bacillus pallidus TK6004 [From this, it is possible to maintain the inside of the machine at high temperature and increase the processing efficiency. Must rely on the action of machines or native fungi. The temperature rise by the machine is certain, but the economic burden is large. Activities by native bacteria are time consuming and uncertain. Therefore, if it is possible to raise the product temperature by the mesophilic bacterium and to maintain the high temperature by the thermophilic bacterium Bacillus pallidus, it would be an inexpensive means to avoid these disadvantages.
- a comparison experiment was performed using the two garbage processors (SANYO: SNS-M15). One was used as a control unit. The other was used as a test machine, and at the start of the experiment, the bacterial powder of the mesophilic bacterium Bacillus subtilis C-3102 was 30 g. The (1 x 1 0 8 c fu / g) was charged. Also, the thermophilic bacterium Bacillus pallidus bacterial powder 4 TK6004 0 g (1 x 1 0 8 cfu / g), was charged in each Namago Mi on. In the experiment, food residue discharged from the cafeteria of the Sagami Plant of Calpis Co., Ltd. was used, and at 14 o'clock every day, 1.5 kg of garbage, twice the manufacturer's recommended amount, was injected. During the test, the temperature and weight were measured and used as a guide for the amount of decomposition.
- Figure 6 shows the transition of the contents weight.
- thermophilic microorganisms By using a combination of mesophilic and thermophilic microorganisms as the microorganisms involved in the decomposition and digestion of the organic waste of the present invention, it is possible to rely on microorganisms derived from conventional naturally generated or treated organic waste. Compared to the conventional method, a spontaneous heat generated by the activity of the mesophilic bacterium achieves a smoother temperature rise, and the thermophilic bacterium is decomposed in the high temperature range at the optimal temperature JP2004 / 000797 Digestion is continuous, and high decomposition treatment efficiency can be achieved.
- the microbial roller is always constant, resulting in the propagation of various bacteria, a decrease in It can eliminate the cause of the decrease in processing efficiency and odor.
- adding mesophilic bacteria does not require heating by an external device up to the high temperature range where the thermophilic bacteria begin to be active, and is an excellent method from the viewpoint of energy saving.
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Abstract
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Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
BR0406706-1A BRPI0406706A (pt) | 2003-01-31 | 2004-01-29 | Métodos para tratamento de resìduo orgânico, agente para tratar resìduo orgânico e microorganismos a serem usados com o mesmo |
EP04706282A EP1598122A4 (en) | 2003-01-31 | 2004-01-29 | PROCESS FOR TREATING ORGANIC WASTE, AGENT FOR TREATING ORGANIC WASTE AND MICROORGANISMS FOR USE THEREFOR |
JP2005504736A JP4503530B2 (ja) | 2003-01-31 | 2004-01-29 | 有機廃棄物処理方法、有機廃棄物処理剤およびそれに用いる微生物 |
US10/543,900 US7846231B2 (en) | 2003-01-31 | 2004-01-29 | Method of treating organic waste, agent for treating organic waste and microorganisms to be used therein |
Applications Claiming Priority (2)
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JP2003-24108 | 2003-01-31 | ||
JP2003024108 | 2003-01-31 |
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WO2004067197A1 true WO2004067197A1 (ja) | 2004-08-12 |
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PCT/JP2004/000797 WO2004067197A1 (ja) | 2003-01-31 | 2004-01-29 | 有機廃棄物処理方法、有機廃棄物処理剤およびそれに用いる微生物 |
Country Status (5)
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US (1) | US7846231B2 (ja) |
EP (2) | EP2774981A1 (ja) |
JP (1) | JP4503530B2 (ja) |
BR (1) | BRPI0406706A (ja) |
WO (1) | WO2004067197A1 (ja) |
Cited By (9)
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JP2006248886A (ja) * | 2005-03-11 | 2006-09-21 | Kazue Watanabe | 環境微生物と酸化剤による植物発生材等、有機廃棄物の迅速無臭堆肥化方法 |
JP2006247601A (ja) * | 2005-03-14 | 2006-09-21 | Tokyo Gas Co Ltd | メタン生成法及びメタン生成装置 |
JP2011223883A (ja) * | 2010-04-15 | 2011-11-10 | National Agriculture & Food Research Organization | 高温性アンモニア酸化細菌およびそれを用いる堆肥の製造方法 |
WO2015020080A1 (ja) * | 2013-08-09 | 2015-02-12 | カルピス株式会社 | バチルス属細菌を利用する農作物の栽培方法 |
JP2015113257A (ja) * | 2013-12-11 | 2015-06-22 | カルピス株式会社 | 循環型農業サイクルへのバチルス属細菌の使用 |
US9365884B2 (en) | 2006-07-20 | 2016-06-14 | Sharp Kabushiki Kaisha | Environmental evaluation installation and environmental evaluation method |
KR101853965B1 (ko) | 2017-11-23 | 2018-05-02 | (주) 참좋은환경 | 음식물 쓰레기 처리용 미생물 제제 |
KR101853964B1 (ko) | 2017-11-23 | 2018-05-02 | (주) 참좋은환경 | 음식물 쓰레기 처리용 미생물 제제 |
KR102239963B1 (ko) * | 2020-04-02 | 2021-04-14 | 주식회사테라바이오 | 기탁번호 kctc18808p로 기탁된 고농도 유기물 발효 및 분해용 기능성 미생물 조성물 배양방법 및 이를 이용한 미생물 조성물 |
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US7846231B2 (en) * | 2003-01-31 | 2010-12-07 | Calpis Co., Ltd. | Method of treating organic waste, agent for treating organic waste and microorganisms to be used therein |
US8268608B2 (en) * | 2006-03-31 | 2012-09-18 | Menicon Co., Ltd. | Method of treating biomass, compost, mulching material for livestock and agent for treating biomass |
TW201102348A (en) * | 2009-07-03 | 2011-01-16 | qiu-zhong Yang | System for circulating-evaporating, treating and recycling palm oil mill effluent |
WO2015037661A1 (ja) | 2013-09-16 | 2015-03-19 | カルピス株式会社 | 微生物による家畜敷料の殺菌方法 |
CN113773986B (zh) * | 2021-08-26 | 2023-07-18 | 郑州轻工业大学 | 一种用于冬季有机固废好氧发酵快速升温的菌剂及其制备方法 |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61281091A (ja) * | 1985-06-03 | 1986-12-11 | 榎本 忠章 | 有機廃棄物を急速発酵処理し堆肥化する方法及びその装置 |
JPH06157176A (ja) * | 1992-04-10 | 1994-06-03 | Towa Kagaku Kk | 微生物肥料およびその製造方法並びに微生物肥料の利用方法 |
JP2001103962A (ja) * | 1999-10-08 | 2001-04-17 | Natl Inst Of Animal Industry | 堆肥化処理からのアンモニア発生を低減するアンモニウム耐性細菌 |
JP2001187375A (ja) * | 1999-10-22 | 2001-07-10 | Aichi Electric Co Ltd | 有機廃棄物の処理方法および処理装置 |
JP2002058471A (ja) * | 2000-08-15 | 2002-02-26 | Denso Corp | 複合微生物群並びに該複合微生物群を利用した有機性廃棄物の分解手段 |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2955608B2 (ja) | 1994-03-15 | 1999-10-04 | トーメイ工業株式会社 | 有機物分解微生物及びそれを用いた有機廃棄物処理方法 |
JPH08217579A (ja) * | 1995-02-10 | 1996-08-27 | Nitto Boseki Co Ltd | 好気性発酵による肥料の製造方法 |
JPH0912387A (ja) | 1995-04-26 | 1997-01-14 | Shikoku Chem Corp | 堆肥化処理剤 |
WO2000042169A1 (fr) * | 1999-01-14 | 2000-07-20 | Gold Kosan Co. Ltd. | Nouveau micro-organisme et utilisation de celui-ci |
US6551804B2 (en) * | 1999-07-12 | 2003-04-22 | E. I. Du Pont De Nemours And Company | Process for preparing 4-cyanopentanoic acid |
US7846231B2 (en) * | 2003-01-31 | 2010-12-07 | Calpis Co., Ltd. | Method of treating organic waste, agent for treating organic waste and microorganisms to be used therein |
-
2004
- 2004-01-29 US US10/543,900 patent/US7846231B2/en active Active
- 2004-01-29 WO PCT/JP2004/000797 patent/WO2004067197A1/ja active Application Filing
- 2004-01-29 BR BR0406706-1A patent/BRPI0406706A/pt not_active Application Discontinuation
- 2004-01-29 EP EP14157200.8A patent/EP2774981A1/en not_active Withdrawn
- 2004-01-29 JP JP2005504736A patent/JP4503530B2/ja not_active Expired - Lifetime
- 2004-01-29 EP EP04706282A patent/EP1598122A4/en not_active Withdrawn
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61281091A (ja) * | 1985-06-03 | 1986-12-11 | 榎本 忠章 | 有機廃棄物を急速発酵処理し堆肥化する方法及びその装置 |
JPH06157176A (ja) * | 1992-04-10 | 1994-06-03 | Towa Kagaku Kk | 微生物肥料およびその製造方法並びに微生物肥料の利用方法 |
JP2001103962A (ja) * | 1999-10-08 | 2001-04-17 | Natl Inst Of Animal Industry | 堆肥化処理からのアンモニア発生を低減するアンモニウム耐性細菌 |
JP2001187375A (ja) * | 1999-10-22 | 2001-07-10 | Aichi Electric Co Ltd | 有機廃棄物の処理方法および処理装置 |
JP2002058471A (ja) * | 2000-08-15 | 2002-02-26 | Denso Corp | 複合微生物群並びに該複合微生物群を利用した有機性廃棄物の分解手段 |
Non-Patent Citations (1)
Title |
---|
See also references of EP1598122A4 * |
Cited By (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006248886A (ja) * | 2005-03-11 | 2006-09-21 | Kazue Watanabe | 環境微生物と酸化剤による植物発生材等、有機廃棄物の迅速無臭堆肥化方法 |
JP2006247601A (ja) * | 2005-03-14 | 2006-09-21 | Tokyo Gas Co Ltd | メタン生成法及びメタン生成装置 |
US9365884B2 (en) | 2006-07-20 | 2016-06-14 | Sharp Kabushiki Kaisha | Environmental evaluation installation and environmental evaluation method |
JP2011223883A (ja) * | 2010-04-15 | 2011-11-10 | National Agriculture & Food Research Organization | 高温性アンモニア酸化細菌およびそれを用いる堆肥の製造方法 |
WO2015020080A1 (ja) * | 2013-08-09 | 2015-02-12 | カルピス株式会社 | バチルス属細菌を利用する農作物の栽培方法 |
JPWO2015020080A1 (ja) * | 2013-08-09 | 2017-03-02 | アサヒカルピスウェルネス株式会社 | バチルス属細菌を利用する農作物の栽培方法 |
US10899677B2 (en) | 2013-08-09 | 2021-01-26 | Asahi Biocycle Co., Ltd. | Method for cultivating crops using bacterium belonging to genus Bacillus |
JP2015113257A (ja) * | 2013-12-11 | 2015-06-22 | カルピス株式会社 | 循環型農業サイクルへのバチルス属細菌の使用 |
US9522852B2 (en) | 2013-12-11 | 2016-12-20 | Asahi Calpis Wellness Co., Ltd. | Use of bacterium of genus Bacillus in circular agricultural cycle |
KR101853965B1 (ko) | 2017-11-23 | 2018-05-02 | (주) 참좋은환경 | 음식물 쓰레기 처리용 미생물 제제 |
KR101853964B1 (ko) | 2017-11-23 | 2018-05-02 | (주) 참좋은환경 | 음식물 쓰레기 처리용 미생물 제제 |
KR102239963B1 (ko) * | 2020-04-02 | 2021-04-14 | 주식회사테라바이오 | 기탁번호 kctc18808p로 기탁된 고농도 유기물 발효 및 분해용 기능성 미생물 조성물 배양방법 및 이를 이용한 미생물 조성물 |
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EP1598122A4 (en) | 2007-05-02 |
JPWO2004067197A1 (ja) | 2006-05-18 |
US20060130545A1 (en) | 2006-06-22 |
JP4503530B2 (ja) | 2010-07-14 |
EP1598122A1 (en) | 2005-11-23 |
BRPI0406706A (pt) | 2005-12-20 |
EP2774981A1 (en) | 2014-09-10 |
US7846231B2 (en) | 2010-12-07 |
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